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Article

Estimation of Groundwater Recharges in Odeda Local Government Area, Ogun State, Nigeria using Empirical Formulae

1
Department of Physics, Federal University of Agriculture, Abeokuta 110001, Nigeria
2
Department of Water Resources Management and Agrometeorology, Federal University of Agriculture, Abeokuta 110124, Nigeria
*
Author to whom correspondence should be addressed.
Challenges 2015, 6(2), 271-281; https://doi.org/10.3390/challe6020271
Submission received: 31 August 2015 / Revised: 1 October 2015 / Accepted: 9 October 2015 / Published: 27 November 2015

Abstract

:
Estimation and forecast of groundwater recharge and capacities of aquifers are essential issues in water resource investigation. In the current research, groundwater recharge and the recharge coefficient were determined through a case study using empirical methods applicable to the tropical zones. The related climatological data between January 1983 and December 2014 were collected from Ogun-Oshun River Basin Development Authority (OORBDA), Ogun State, Nigeria. Using empirical formulae. The results showed that groundwater recharge was 194.7 mm per year, evapotranspiration was 1296.2 mm per year, and the recharge coefficient was 20.2% for the study area. The result showed that about 11% of rainfall infiltrated the aquifer, 73% was lost to evapotranspiration, and 36% ended up as run-off. Correlation between climatic parameters and groundwater recharge showed the highest correlation between recharge and rainfall. Temperature, humidity, solar radiation and evapotranspiraton were obtained at the 0.01 significance level; the results of linear regressions proved that precipitation has a significant effect (with R2 = 0.983) on estimated recharge.

1. Introduction

In arid and semi-arid regions, the search for water which are under increasing stress from the growing human population, poses a great challenge due to its scarcity [1]. Groundwater, as a dynamic system, is located beneath the Earth surface and moves under the control of many factors, which are influenced by forces that are dependent on hydrogeology, hydrology, and climatology [2]. Recharge, as one of the factors controlling the situation and fluctuation of groundwater, is an important parameter that needs to be assessed more fully. Recharge occurring in small and large scales, spatially and temporally, is influenced by several factors, such as meteorology, soil characteristics, geology, surface cover, slope, and depth of the groundwater level [3,4,5]. Groundwater recharge estimation from precipitation is an integral part of hydrology and hydrogeology [6].
Although, precipitation is the most important source of groundwater recharge [7] the accuracy of currently attainable techniques for measuring recharge are not completely acceptable.
Comparative analysis of empirical formulae to estimate recharge which is a prerequisite for groundwater resource management was carried out [8]. Estimation of groundwater recharge was derived from rainfall data obtained from Ogun-Oshun River Basin Development Authority (OORBDA) using three empirical formulae, which include the empirical methods of [7,9,10]. The result revealed that the three formulae used gave comparable results, hence their conclusion that any of the formulae can be used for groundwater estimation. Additionally, in order to validate the formulae, the groundwater recharge and capacity of aquifers in Malaysia was estimated using empirical formulae [9] and obtained a recharge of 326.39 mm was obtained for the area [11].
In measuring groundwater recharge, indirect methods are employed since there are no universally accepted standard methods. However, methods for determining the groundwater recharges have been classified into three groups namely: Physical Model method, obtained when the recharge is calculated from the base flow; Chemical model method, which is used when the measurements of water soluble substances are considered; and Numerical model methods, such as HELP, RORA, PART, WEAP, WTF, PUISE, HYSEP and so on, which can be used in the estimation of groundwater recharges for various climates such as in arid, semiarid, and tropical regions albeit each with its own advantages and disadvantages [12].

2. The Study Area

Odeda Local Government Area is located on the outskirts of Abeokuta, an ancient city in the southwestern part of Nigeria, extending from longitude 3.3899E to 3.47950E and latitude 7.1745N to 7.2300N. Abeokuta is located in Ogun State, Southwestern Nigeria, as shown in Figure 1.
The study area is characterized by a tropical climate with distinct wet and dry seasons. The wet season is associated with the relative prevalence of the Moist Maritime Southerly Monsoon from the Atlantic Ocean, while the dry season is predicated by the Continental North Easterly harmattan winds from the Sahara desert. The area is located within a region characterized by a bimodal rainfall pattern (commencing in March; plentiful in July and September, with a short dry spell in August). The long dry season extends from November to March. Annual rainfall ranges between 1400 and 1500 mm in Abeokuta and environs. The region is characterized by relatively high temperature with a mean annual air temperature being about 30 °C. The greatest variation in temperature is experienced in July (25.7 °C) and in February (30.2 °C). Humidity is lowest (37%–54%) at the peak of dry season in February and highest at the peak of the rainy season between June and September (78%–85%).
The study area is underlain by basement complex, and the basement complex rocks of Nigeria are well-represented in the selected study area of Ogun State. These rocks are of Precambrian to early Palaeozoic age and they extend from the northeastern part of Ogun State running southwest and dipping towards the coast [13].
The basement complex metamorphic rocks are characterized by various folds, structures of various degrees of complexity, faults and foliation. These structural features have a predominant North-South or North-North-East-South-South-West (NNE-SSW) orientation which is particularly strong within the low grade metamorphic. The common metamorphic rocks encountered are gneiss, schist, quartzite and amphiboles. The study area is characterized by various rock types ranging from, granite granitic gneiss and pegmatite. The individual rocks have various hydro-geologic characteristics and belongs to the stable plate which was not subjected to intense tectonics in the past. Therefore, the underground faulting system is minimal and this has contributed to the problem of underground water occurrence in this area.
Figure 1. Location Map showing the study area.
Figure 1. Location Map showing the study area.
Challenges 06 00271 g001

3. Methodology

Owing to the non-availability of meteorological stations in the study area, Ogun Oshun River Basin Development Authority (OORBDA) meteorological station was used; parameters collected from OORBDA weather station were; minimum and maximum temperature, sunshine hour, relative humidity wind speed, and rainfall data.
Thirty-two (32) years of weather parameters were collected from OORBDA weather station. These were used to calculate the recharge, evapotranspiration, recharge coefficient and run-off using empirical formulae.
The potential evapotranspiration (PE) was determined using CROPWAT version 8.0 based on FAO Penman-Moteithe formula.

3.1. Evapotranspiration

Evapotranspiration is regarded as to the sum of evaporation and transpiration. It is a climatic index integrating the effect of air temperature, humidity, wind speed, and solar radiation. CROPWAT software version 8.0 was used to estimate evapotranspiration. The software is based on the FAO Penman-Monteith formula [14].

3.2. Estimation of Groundwater Recharge

Estimation of groundwater recharge of the study area was conducted using a modified version of [9] for tropical regions based on water level fluctuation and rainfall depth [14,15]. The equation is given as:
R = 1.35 ( P 14 ) 0.5
where R is the net recharge due to precipitation in inches, and P is the precipitation in inches. These can be converted to millimeters (mm).

3.3. Recharge Coefficients

The value of the recharge coefficient is defined as the ratio of recharge to effective rainfall; it is expressed in percentage [15] as:
R c o e f f i c i e n t = R P e %
where R is the recharge and Pe is the effective rainfall.

3.4. Estimating Direct Runoff

Estimated runoff for water budget was developed by [16], and is given as:
R o f f = 0.85 × P 30.5
where Roff is the direct runoff and P is the precipitation.

3.5. Co-Integration Analysis

The climatic data was analyzed using co-integration analysis. The analysis involves a unit root test performed on levels, the first difference and the second difference were used to determine whether the individual input series are stationary and exhibit similar statistical properties. It must be noted that regressing a non-stationary time series data over another non-stationary time series data gives a spurious or unreliable regression. To correct for this, a unit root test is performed [17].
A time series is stationary when X(t1), X(t2),…, X(tn) is the same as the joint distribution of any set of X(t1+k), X(t2+k),…, X(tn+k), for all n and k.
Y t = p Y t 1 + U t
where p ≤ 1 and U is the white noise error.
If the estimated p is statistically equal to 1 when Yt is regressed on Yt−1, then Yt is non-stationary; that is, has no unit root (I (0)).
The Augmented Dickey–Fuller (ADF) test was used to test for the stationarity of the data. The test consists of the following regression:
Δ Y τ = β 1 + β 2 τ + δ Y τ 1 α τ = 1 n Δ Y τ + ε τ
where:
ε τ = Δ Y t 1 = ( Y t 1 Y t 2 ) , Δ Y t 2 = ( Y t 2 Y t 3 )
The Johansen procedure was used to test for the number of co-integration vectors in the model. The Johansen technique was used not only because it is vector auto-regressive-based but because it performs better in multivariate models [18]. If Xt and Yt are then co-integrated, their short-run dynamics can be described by an error correction model (ECM). The theory states that if two variables, Y and X, are co-integrated, then the relationship between them can be expressed as an ECM [18]. The co-integration model is given as:
P t = β 0 + β 1 R t + β 2 S R t + β 4 M T t + β 5 X T t + β 6 E T t + U t

3.6. Correlation and Regression Analyses

Pearson correlation coefficient was used to evaluate the strength of the relationship between meteorological factors. The impact of independent variables (i.e., humidity, temperature, rainfall, wind speed, and duration of daily solar radiation) on estimated recharge was evaluated using linear regression.

4. Results

The methods discussed were used to estimate all parameters from January 1983 to December 2014. This covers a period of thirty-two (32) years. Table 1 shows the amount of calculated groundwater recharge, evapotranspiration, the recharge coefficient, and surface runoff. The ratio of recharge to total precipitation is 11%, which according to [16], is classified as a low rate of recharge. It is proved that aside from precipitation (with the high rate), other parameters (such as surface cover) also have a key role [4,5] in recharge. Table 1 shows the hydrological data of the study area for 32 years, for 1983 to 2014.
Table 1. Hydrological data of the study area for 32 years (1983 to 2014).
Table 1. Hydrological data of the study area for 32 years (1983 to 2014).
YearP (mm)R (mm)Min. Temp. (°C)Max. Temp. (°C)ET (mm/yr)Run OffRcoeff (%)
1983901.6159.022.332.11284.8763.823
19841032.4177.020.031.91252.0874.920
19851185.7196.021.531.91116.91005.221
19861210.7199.024.831.91394.31026.520
19871224.5199.426.437.71525.71038.221
19881576.1237.820.936.31219.11337.019
19891222.6200.319.437.12000.21036.620
19901336.1213.020.437.62029.41133.120
19911185.0195.920.136.51328.61004.720
19921445.6191.218.537.41332.31226.220
1993941.2164.823.437.21357.8797.422
19941009.6174.231.437.31434.5855.521
19951244.7202.930.837.31401.61055.420
19961254.6204.021.837.4978.21063.820
19971233.5201.729.937.41237.41045.920
1998895.4158.322.034.81076.8758.522
19991037.5177.913.831.9981.9879.223
2000948.5165.516.733.1960.0803.222
2001950.0165.515.333.31043.9805.621
20021736.5252.910.233.01284.91473.418
20031449.7225.112.834.31325.01229.720
20041112.7187.222.831.11262.9943.220
20051112.7187.213.433.01200.9943.220
20061236.2202.023.731.1949.01048.221
20071943.9273.126.032.21189.91651.418
2008848.9151.025.926.71215.5719.022
20091189.9197.826.030.51376.11008.720
20101233.9201.725.836.41398.01046.221
20111497.7223.525.436.61248.31245.015
20121241.5204.225.036.81255.61052.715
2013929.2163.024.935.51379.7787.222
20141058.0180.322.932.21474.6896.721
In Table 1, P is the annual precipitation, R is the annual groundwater recharge (mm), ET is the evapotranspiration (mm/year), Min. T is the minimum temperature (°C), Max. T is the maximum temperature (°C), and Rcoeff. is the recharge coefficient (%).
Figure 2 shows the annual rainfall, recharge, evapotranspiration, and temperature from 1983–2014. Groundwater recharge increases with precipitation and shows the same trend throughout the years. However, evapotranspiration shows variation in trend throughout the study area. This is expected because evapotranspiration is a function of temperature, which showed a remarkable change throughout the years, in the study area. Typically, low rainfall causes low groundwater recharge infiltrating into the aquifer, this is due to increase in temperature and evapotranspiration and vice versa.
Figure 2. Total annual precipitation, groundwater recharge, evapotranspiration, and temperature.
Figure 2. Total annual precipitation, groundwater recharge, evapotranspiration, and temperature.
Challenges 06 00271 g002
There are objections to the use of either of these data since the data from the greater area is more useful for national decision-makers; the present method would be of great help to the local authority for future sustainable development of the region. The percentage of evapotranspiration, runoff, and recharge in the study area are 73%, 16%, and 11%, respectively. Typically low recharge causes high runoff over the surface.

4.1. Co-Integration

Table 2 represents the result of the ADF test. It is evident that recharge is non-stationary and likewise, the annual rainfall, but are stationary after the second differencing. Other climatic parameters are non-stationary. It has been ascertained that the variables exhibit unit root I (1) (non-stationary) at their levels, but stationarity after differencing, hence there exists a long run relationship between the climate parameters.
Table 2. Result of stationary test from the Augmented Dickey-Fuller Test.
Table 2. Result of stationary test from the Augmented Dickey-Fuller Test.
Climate ParametersLevel1st Difference2nd DifferenceDecision
Precipitation−4.364246−5.394125−3.565695Stationary
Recharge−4.224929−5.074373−3.699143Stationary
Min Temperature−2.302965−5.385516−9.299585Non-stationary
Max Temperature−2.174135−4.069986−4.069986Non-stationary
Evapotranspiration−2.761985−5.987190−8.289337Non-stationary
Relative Humidity−2.604266−4.506285−6.032715Non-stationary
Solar Radiation−3.820166−6.558539−8.069424Non-stationary
Critical level (1%): −3.6752
Table 3. Johansen co-integration result.
Table 3. Johansen co-integration result.
Eigen ValueLikelihood 5% Critical 1% CriticalHypothesized No. of CE(s)
0.751784105.243994.15103.18None **
0.59470664.8336968.5276.07At most 1
0.48165638.6425347.2154.46At most 2
0.26467019.5861729.6835.65At most 3
0.22368310.6705415.4120.04At most 4
0.1084153.3278823.766.65At most 5
** denotes rejection of the hypothesis at 5% (1%) significant level. Likelihood ratio test indicates 1 co–integration equation at 5% significant level.
Table 3 shows the Johansen co-integration results. The likelihood ratio shows that there is only one co-integrating (CI) equation in the analysis. The CI equation was based on the conformity of the coefficients with economic theory and its statistical significance. From the equation, the precipitation variable was considered to have a significant effect on estimated recharge in the study area during the period studied.
The adjusted R2 shows that about 98% of the variation in recharge is explained by the effects of precipitation (Table 4). This shows that an increase in rainfall value will cause the recharge value to increase and vice versa.
Table 4. Results from the Error Correction Model.
Table 4. Results from the Error Correction Model.
VariableCoefficientStandard. Errort-StatisticsProbability
Recharge11.138990.35674231.224190.0000
Solar Radiation−6.1771487.792169−0.7927380.4354
Min Temperature0.8900653.5950270.2475820.8065
Max Temperature2.8185257.3025450.3859650.7028
Evapotranspiration−12.5519037.99302−0.3303740.7439
Constant−935.5960229.9052−4.0694860.0004
Dependent variable: precipitation. R 2 = 0.977; Durbin Watson stat: 1.583017; F-stat: 212.6064

4.2. Correlation and Regression Analysis

This was to study the correlation between estimated recharge and climate parameters. Table 5 shows the Pearson correlation coefficient for meteorological parameters (1983–2014) on estimated recharge. The results showed that evapotranspiration was correlated with solar radiation at the 0.01 significance level, with R2 = 0.647. Additionally, estimated recharge was correlated with precipitation at the 0.01 level (R2 = 0.943). There is no significance at any level among the other parameters with regression analysis, which was conducted to evaluate the effect of climate parameters on estimated recharge. It was observed from Table 4 that all parameters showed minimal relationships to estimated recharge, except precipitation, which showed a dominant role of rainfall percolation of water into the ground in the study area. Table 5 and Table 6 show the Pearson correlation coefficient for meteorological parameters, and regression analysis of weather parameters on the estimated recharge in the study area.
Table 5. Pearson correlation coefficient for meteorological parameters.
Table 5. Pearson correlation coefficient for meteorological parameters.
Precipitation
(mm)
Recharge
(mm)
Min Temp.
(°C)
Max Temp
(°C)
ET
(mm)
Rel. Hum.
(%)
Precipitation (mm)10.9430.2790.2580.059−0.050
Recharge (mm)0.94310.4330.2310.0640.051
Min. Temp. (°C)0.1040.08510.2610.327−0.036
Max Temp. (°C)0.2440.2630.20510.0190.303
ET (mm)0.0160.0460.1650.41310.019
Rel. Hum. (%)0.1190.092−0.1180.389−0.0031
Solar Rad.−0.0130.023−0.0470.2050.647−0.017
Table 6. Regression analysis of weather parameters on estimated recharge.
Table 6. Regression analysis of weather parameters on estimated recharge.
Weathered Parameter / RechargeDetermination Coefficient (r 2)Regression Equation
Precipitation (mm)0.983Y = −962.462 + 11.2228X
Min. Temperature (°C)0.007Y = 20.2466 + 8.42E − 03X
Max. Temperature (°C)0.069Y = 31.5017 + 1.42E − 02X
Relative Humidity (%)0.008Y = 78.5326 + 1.22E − 0.2X
Solar Radiation0.001Y = 15.0630 + 1.39E − 0.3X

5. Conclusions

The estimation of groundwater recharges have been carried out in Odeda Local Government Area, Ogun State, Nigeria. The methods used have greatly helped in estimating the groundwater recharges in the area. The annual mean groundwater recharge for 32 years (1983–2014) has been estimated to be 194.7 mm per annum. The mean of the recharge coefficient is 20.2%, the rate of evapotranspiration is about 73%, and groundwater recharge is about 11%. Therefore, 16% of rainfall water makes some allowance for runoff (and/or interflow) in the study area. The study shows that there is variability in climate parameters. The study also shows that the climate has a significant effect on groundwater resources. This is clearly revealed in the rainfall variable; however, evapotranspiration and solar radiation have a relationship with each other. The study also shows that the change in climate has a significant effect on recharge. This is clearly revealed in the rainfall variable; however, temperature seems to be an unimportant variable of climate in the determination of recharge in the study area. The correlation between parameters showed the highest positive correlation between recharge and rainfall. In addition, correlation between temperature and humidity, solar radiation, and et are at the 0.01 level. Results of linear regressions proved precipitation has a significant effect (with R2 = 0.983) on the estimation of recharge.

Author Contributions

Victor Makinde conceived the research, Oluseyi Adeleke carried out the research which was thoroughly supervised by Victor Makinde and Ayobami Eruola. Oluwaseun Dada helped in acquiring the data. Oluseyi Adeleke, Akintayo Ojo and Taiwo Aluko analysed the data. Oluseyi Adeleke wrote the manuscript, Akintayo Ojo reviewed and adapted the manuscript to fit the style of the journal.

Conflicts of Interest

The authors declare no conflicts of interest.

References

  1. Kishan, S.R.; Anil, K.M.; George, P.; Rakesh, K. Estimation of ground water recharge in Shankergarh block of Allahabad (India) using remote sensing and statistical approach. Glob. J. Sci. Eng. Technol. 2012, 1, 34–48. [Google Scholar]
  2. Kumar, C.P. Estimation of natural ground water recharge. ISH J. Hydraulic Eng. 1977, 3, 61–74. [Google Scholar] [CrossRef]
  3. Bouwer, H. Groundwater Hydrology; McGraw-Hill Book Company: New York, NY, USA, 1978. [Google Scholar]
  4. Shukla, S.; Jaber, F.H. Groundwater Recharge from Agricultural Areas in the Flatwoods Regionof South Florida. Available online: http://ufdcimages.uflib.ufl.edu/IR/00/00/15/42/00001/AE39900.pdf (accessed on 7 May 2015).
  5. Sumioka, S.S.; Bauer, H.H. Estimating ground-water recharge from precipitation on Whidbey and Camano Islands, Island County, Washington, water years 1998 and 1999. In Water-Resources Investigations Report, 03-4101; Tacoma, W.A., Ed.; U.S. Geological Survey: Pembroke, MA, USA, 2003. [Google Scholar]
  6. Xi, C.; Zhang, Z.; Zhang, X.; Chen, Y.; Qian, M.; Peng, S. Estimation of groundwater recharge from precipitation and evapotranspiration by Lysimeter measurement and soil moisture model. J. Hydrol. Eng. 2008, 13, 333–340. [Google Scholar]
  7. Kumar, C.P.; Seethapathi, P.V. Assessment of natural ground water recharge in upper Ganga Canal command area. J. Appl. Hydrol. 2002, 15, 13–20. [Google Scholar]
  8. Oke, M.O.; Martins, O.; Idowu, O.; Aiyelokun, O. Comparative analysis of empirical formulae used in groundwater recharge in Ogun-Oshun River Basins. J. Sci. Res. Repo. 2013, 2, 692–710. [Google Scholar] [CrossRef] [PubMed]
  9. Chaturvedi, R.S. A note on the investigation of ground water resources in western districts of Uttar Pradesh. In Annual Report; U.P. Irrigation Research Institute: Bahadrabad, India, 1973; pp. 86–122. [Google Scholar]
  10. Kumar, C.P. Groundwater Assessment methodology; National Institute of Hydrology: Roorkee, India, 2009. [Google Scholar]
  11. Saghravani, S.R.; Ismail, Y.; Sa’ari, M.; Saghravani, S.F. Estimating groundwater recharge using empirical method: A case study in the tropical zone. Sains Malaysiana 2013, 42, 553–560. [Google Scholar]
  12. Risser, D.W.; Gburek, W.J.; Folmar, G.J. Comparison of recharge estimates at a small watershed in east-central Pennsylvania, USA. Hydrogeol. J. 2008, 2008, 17, 287–298. [Google Scholar] [CrossRef]
  13. Ako, B.D. Geophysical prospecting for groundwater in parts of south-western Nigeria. Ph.D. Thesis, Department of Geology, University of Ife, Ile-Ife, Nigeria, 1979. [Google Scholar]
  14. Allen, R.; Pereira, L.A.; Raes, D.; Smith, M. Crop evapotranspiration. In FAO Irrigation and Drainage Paper No. 56; FAO: Rome, Italy, 1998. [Google Scholar]
  15. Misstear, B.D.R.; Brown, L.; Daly, D. A methodology for making initial estimates of groundwater recharge from groundwater vulnerability mapping. Hydrogeol. J. 2009, 17, 275–285. [Google Scholar] [CrossRef]
  16. Muteraja, K.N. Applied Hydrology; Tata MGraw-Hill: New Delhi, India, 1986. [Google Scholar]
  17. Ayinde, E.O.; Muchie, M.; Olatunji, G.B. Effect of climate change on Agricultural productivity in Nigeria: A co-integration model approach. J. Hum. Ecol. 2011, 35, 189–194. [Google Scholar]
  18. Maddala, G.S. Introduction to Econometrics, 3rd Ed. ed; John Wiley and Sons Ltd: New York, NY, USA, 2001. [Google Scholar]

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MDPI and ACS Style

Adeleke, O.O.; Makinde, V.; Eruola, A.O.; Dada, O.F.; Ojo, A.O.; Aluko, T.J. Estimation of Groundwater Recharges in Odeda Local Government Area, Ogun State, Nigeria using Empirical Formulae. Challenges 2015, 6, 271-281. https://doi.org/10.3390/challe6020271

AMA Style

Adeleke OO, Makinde V, Eruola AO, Dada OF, Ojo AO, Aluko TJ. Estimation of Groundwater Recharges in Odeda Local Government Area, Ogun State, Nigeria using Empirical Formulae. Challenges. 2015; 6(2):271-281. https://doi.org/10.3390/challe6020271

Chicago/Turabian Style

Adeleke, Oluseyi O., Victor Makinde, Ayobami O. Eruola, Oluwaseun F. Dada, Akintayo O. Ojo, and Taiwo J. Aluko. 2015. "Estimation of Groundwater Recharges in Odeda Local Government Area, Ogun State, Nigeria using Empirical Formulae" Challenges 6, no. 2: 271-281. https://doi.org/10.3390/challe6020271

APA Style

Adeleke, O. O., Makinde, V., Eruola, A. O., Dada, O. F., Ojo, A. O., & Aluko, T. J. (2015). Estimation of Groundwater Recharges in Odeda Local Government Area, Ogun State, Nigeria using Empirical Formulae. Challenges, 6(2), 271-281. https://doi.org/10.3390/challe6020271

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